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The Kinetics of Acetylcholinesterase Inhibition
and the Influence of Fluoride and Fluoride Complexes on the Permeability
of Erythrocyte Membranes
Dissertation to receive Ph.D.
in Chemistry from the University of Hamburg
By Johannes Westendorf
Hamburg, Germany - 1975
(Click here
to read Westendorf's thesis)
Reviewer:
Prof Dr. A. Knappwost
Co-Reviewers:
Prof, Dr, Malomy Prof,
DR, Strehlow Prof,
Dr. Hilz Prof
Dr. Gercken
The oral defense took place on 2/18/1975
A Foreword intended to place the Westendorf research in current context
indicating why it is relevant to a wide range of contemporary health
and behavioral problems has been prepared by Myron J. Coplan and Roger
D. Masters whose credentials are also attached.
Mikecoplan@aol.com Roger.D.Masters@Dartmouth.edu
Foreword
by MJ Coplan and RD Masters, April 2001 Westendorf's
30-year PhD research work is important for reasons beyond its specific
scientific findings. First his work was motivated by the assumption
that ingested fluoride was beneficial. Knappwost, his thesis supervisor,
believed that fluoride in saliva afforded protection against tooth
decay and was seeking a means of enhancing the output of fluoride-bearing
saliva for that purpose. Therefore, it can hardly be said that Westendorf's
work was biased against water fluoridation.
Second, Westendorf's research was based an knowledge
that fluoride ion is an enzyme inhibitor. Indeed, that feature of
ingested fluoride seemed to offer multiple benefits. Knappwost believed
that ingested fluoride, by inhibiting cholinesterase, could achieve
both greater expression of total saliva and an increase in its fluoride
content. The research of his student quite logically examined different
forms of ingestible fluoride for their effect on several variants
of cholinesterase, Westendorf's results showed that fluoride in
the form of the silicofluoride complex (SiF), as well as several
other complexes, was a substantially more powerful inhibitor of
cholinesterases than the simple fluoride ion released by sodium
fluoride (NaF). This was simply an objective finding.
Third, to account for the more powerful inhibition
effect of SiF, Westendorf studied the course of its fluoride release
in fine detail. He found that under physiological conditions, dissociation
was no more than 66% in the concentration range considered "optimum"
for fluoridated water by United States health authorities. If the
released fluoride came uniformly from all of the initially injected
SiF, the molar concentration of the residual non-dissociated species
would be the same as that of the injected SiF. It would follow that
dilution of fluosilicic acid to a nominal 1 part per million of
free fluoride in water at pH 7.4 induces each [SiF6]2- to release
4 fluorides to be replaced by hydroxyls. The partially dissociated
residue would be the ion [SiF2(OH)4]2- which would then be present
in the water at the same concentration as the originally introduced
SiF. The biological consequences of ingesting such a species are
probably not innocuous, with enzyme inhibition being only one of
several possibilities.
Westendorf's visualized course of SiF dissociation,
based on actual experimental evidence, is materially at odds with
the dissociation route assumed by US EPA and CDC, based on theory.
In judging the reliability of the theoretical approach and claims
of health safety presented by these government agencies, one should
be aware that both the nature of the complicated mixture called
"fluosilicic acid" and the course of its dissociation upon dilution
remain unresolved despite nearly a century of research. Two recent
documents demonstrate this. In the first, an expert in the recovery
of fluoride in phosphate rock processing, addressing a group of
his peers at a 1999 International Fertilizer Association (a) meeting
held in the former USSR, said:
"The chemical formula of fluosilicic acid is H2SiF6. However,
things are not as simple as that due to the fact that rarely is
fluosilicic acid present as pure H2SiF6. . . There are well reported
references to the existence of H2SiF6 SiF4. . . Hereon in this
presentation, FSA [fluosilicic acid] means a mixture of HF, H2SiF6
and H2SiF6 SiF4."
This is a highly significant statement coming from someone who
ought to know the subject under discussion. It means that a key
intermediate dissociation product postulated by CDC and EPA theories
to be transient species only fleetingly after SiF is introduced
into the water at the water plant, may be present in concentrated
fluosilicic acid before dissociation begins. Such a starting condition
would cast serious doubt on the postulated theoretical equations
predicting "virtually 100%" dissociation that supposedly "guarantee"
no adverse health effects from undissociated SiF residues in drinking
water treated with these compounds.
Equally important is a letter (b) dated March 15,
2001, written by the Director of the EPA Water Supply and Water
Resources Division, which concludes with the statement:
"In January, representatives from the [EPA] Office of Research
and Development (ORD) and the Office of Science and Technology
and Ground Water and Drinking Water met to discuss a number of
water related issues including Fluoridation. Several fluoride
chemistry related research needs were identified including; (1)
accurate and precise values for the stability constants of mixed
fluorohydroxo complexes with aluminum (III), iron (III) and other
metal cations likely to be found under drinking water conditions
and (2) a kinetic model for the dissociation and hydrolysis of
fluosilicates and stepwise equilibrium constants for the partial
hydrolysis products."
In plain English, senior EPA research staff now believe their staff
needs to go back to the lab for at least another year or two to
find out if the EPA's longstanding confidence in the "virtually
total" dissociation of SiFs may have been misplaced. Whatever the
outcome may be of their new study of SiF dissociation, it is clear
the EPA does not intend to perform animal tests to ascertain health
effects of chronic ingestion of SiF treated water under controlled
conditions.
Animal experiments according to accepted toxicology
testing protocols would be the logical way to examine health effects
of enzyme inhibition by SiF that Westendorf observed at the cellular
level. Three published reports bearing directly on this matter should
be noted. In the early 1930s, the Ohio agriculture department wanted
to develop a replacement for bone meal as a source of calcium and
phosphorus in the feed ration of farm animals. Natural "rock phosphate,"
comprising largely calcium phosphate, was a candidate, but it was
known to carry about 2 to 5% of fluoride bound in some chemical
form. Thus it was necessary to study possible adverse health effects
due to ingestion of fluoride from several sources.
A report (c) issued in 1935 compared health effects
primarily from calcium fluoride, sodium fluoride, and rock phosphate.
Highly significant for present purposes was one small experiment
that included sodium fluosilicate. With equal dosage and equal amounts
of fluoride retained, rats fed sodium fluosilicate excreted three
times as much non-retained fluoride in urine as rats fed sodium
fluoride, who eliminated more fluoride in feces. Apparently about
three times as much fluoride had crossed the gut/blood membrane
into the bloodstream from SiF than from NaF. A second report, this
one by the US PHS, (d) was published about ten years after water
fluoridation had begun. The study compared the time, starting from
the date of fluoridation either with sodium fluosilicate or sodium
fluoride, for urinary fluoride level to reach equilibrium with ingested
fluoride from fluoridated water. The study populations were boys
and men. There were two noteworthy results. First, for either fluoridating
agent, urine fluoride levels in older males reached equilibrium
with ingested fluoride levels sooner than in younger males. The
longer time for young males can be accounted for by the fact that
the weight of the older males was essentially constant, while the
younger males were adding bone mass over the several years of the
experiment. The bodies of younger males were therefore providing
a time-related increase in storage compartment capacity for ingested
fluoride.
A more important finding was that for the younger
males it took longer for their urine level of fluoride to reach
equilibrium with ingested water fluoride from SiF than from NaF.
Apparently in growing boys SiF fluoride must have been metabolizing
differently from NaF fluoride.
A third relevant study (e), conducted around the
same time as Westendorf's research, involved feeding water treated
with the same fluosilicic acid used to fluoridate the local water
supply to squirrel monkeys for up to 14 months. Morphological and
cytochemical effects were reported for the liver, kidney, and nervous
system due to ingestion of 1-5 ppm of fluoride in water. Although
the study did not compare results from exposure to NaF, the report
emphasizes the fact that the kidneys of monkeys ingesting SiF treated
drinking water "Éshowed significant cytochemical changes, especially
in the animals on 5 PPM fluoride intake in their drinking water."
The report later observes that work by others in
the 1940s and 1950s "Éshowed that fluoride has an inhibitive effect
on the activity of succinate dehydrogenase. These studies indicate
that under the effect of fluoride intake, a serious metabolic distress
may develop in the kidneys." In concluding, the report notes that
"Earlier, some workers had also indicated that inorganic fluorides
have a strongly adverse effect on the activity of some enzymes and
of these, mitochondrial enzymes, acid and alkaline phosphatases
and ATP-utilizing enzymes and aldolase may be the most affected
(Batenburg & Van den Bergh, 1972; Katz & Tenenhouse, 1973)."
This study of squirrel monkeys is a rare (possibly
singular) American experiment with SiF. If the research team had
known that Westendorf was finding greater effects of silicofluoride
than sodium fluoride on enzyme activity at virtually the same moment,
the U.S. study might have taken a different turn. In any case, two
of these three American experiments compared effects from NaF and
SiF, and both found that SiF and NaF do not produce the same
effect. Moreover, all three studies found the strongest adverse
clinical effect of silicofluoride in the kidney. But damage to the
kidney is hardly the only possible health effect of ingested SiF.
"Life" involves an incalculable number of chemically
active molecules initiating, continuing and terminating a bewildering
variety of chemical events. Throughout this panoply of events and
in every organ where they occur, various enzymes play crucial roles.
A particularly important example is the quenching by enzymes of
muscle stimulation induced by the neurotransmitter acetylcholine
(ACh), an ester comprising the acetyl moiety bound by an oxygen
bridge to the choline molecule. The principal "quenching" enzyme,
acetylycholinesterase (AChE), comes in several variations and the
ACh/Ache dyads operate in numerous ways in many organs. Related
enzymes called pseudocholinesterases are found in serum and include
the butyrylcholinesterases.
At latest count over 7,000 enzymes have been detected
and catalogued, (f) and there is no reason to suppose that the effect
of SiF is limited only to a sub-class. In any event, one would be
hard put to identify a more important enzyme subclass than "esterases,"
which cleave molecules called "esters" at the right time and place
in the healthy organism. While a great deal is known about many
of the ways these enzymes function, there are still large knowledge
gaps to be filled. To do just that, an extensive survey of contemporary
knowledge about cholinesterases has recently been published (g)
by an employee of the Office of Prevention, Pesticides and Toxic
Substances in EPA's Health Effects Division. The published article
carries this disclaimer:
"Although this article was written as part of the author's official
duties as an EPA scientist, the opinions and conclusions expressed
in it are his alone, and do not reflect the position of the Environmental
Protection Agency."
Dementi's review deserves a great deal of attention, so one wonders
why it was not published as official work of the EPA. The EPA has
acknowledged (h) that it has no data on health effects of the SiFs,
shown by Westendorf to be a significant cholinesterase inhibitor
and being added to the diets of 140 million people at the rate of
200,000 tons a year. The many different biochemical responses this
dosage can be expected to elicit may well support a recently published
(l) hypothesis proposing an explanation for Fibromyalgia, Multiple
Chemical Sensitivity, and Chronic Fatigue Syndrome. It is not at
all unlikely that chronic ingestion of SiF treated water also bears
on ADD/ADHD, teen violence, and even some of the ambiguities associated
with Gulf War Syndrome.
Common sense suggests that wide-spread, albeit
clinically vague, adverse health effects should be expected when
a strong enzyme inhibitor is added to the daily diets of over half
of US residents, as would be the case given the results of the research
work described herein. With millions of people suffering from one
or another poorly understood condition with likely roots in environmental
toxins, it is time to reexamine entrenched governmental doctrines
in the light of Westendorf's research which, while 30 years old,
has received little or no attention heretofore.
(Read Westendorf's thesis)
Notes and Credits
NOTE 1. The following English language text,
translated from the German in which it was written by Dr. Johannes
Westendorf, (Toxicology Department, Eppendorf-Hamburg University
Hospital) was submitted to him in March 2001 for his comments with
a series of questions. This was his response.
"With respect to my thesis I finished this kind
of work in 1976, when I changed to the Medical faculty, where
I still am. After my thesis I continued the work on fluoride for
another year and we especially worked on the stability of hexafluoro
complexes of silicon and iron. We used radioactive isotopes, such
as F-18 and Si-31 . . . when we analyzed the electrophoretic mobility.
In the presence of silicon and iron, fluoride ions showed a different
mobility compared to fluoride [ion] itself. Unfortunately I have
no access to these old experiments and we did not publish it.
. . . During hydrolysis we got a continuous
shifting of the mobility, indicating that the different forms
of hydrolysis with 2-6 fluorine at the Si are present at the same
time, ending up at the more stable form of Si(OH)4F2. If we increased
the pH to 9 and higher, a total hydrolysis occurs.
...In answering your final paragraph I can say:
1) The English translation of my thesis is excellent.
2) I have no evidence from others that contradict to my old findings.
3) Your idea of the enzyme inhibition by the complex could be
right, however slight changes in the pH, caused by the hydrolysis
of hexafluorosilicate, would also result in an increased inhibition
of acetylcholinesterase. Nevertheless, I agree with you that the
toxicology of hexafluorosilicate should be investigated because
it may be different from simple fluoride.
Please let me know if I can be of further assistance
to you. Johannes Westendorf" Westendorf@uke.uni-hamburg.de
NOTE II. Although the main body of the Westendorf
thesis was not published in a circulating journal as such, three
short articles based on this work were. Copies of the two most relevant
ones appear at the end of the English text of the full thesis.
CREDITS: The thesis was called to our attention
and photocopied from the document on file in the archives at the
University of Hamburg by Peter Meiers (Weissenburgerstr. 28, D-66113
Saarbrucken; the translation was prepared by Jakob von Moltke (Dartmouth
College); final proof editing was done by Myron Coplan with the
aid of Norman Mancuso.
References:
a) Smith, PA. "History of Fluorine Recovery Processes":
Paper delivered at the IFA Technical Sub-Committee and Committee
Meeting in Novgorord, Russia; Sept 15-17, 1999 (http://www.fertilizer.org/ifa/publicat/techpprs/tech0999.asp)
b) Gutierrez, SB. (signed by Thurnau RC); Letter
from the Director of the US EPA National Risk Management Laboratory
to Roger D. Masters, dated March 15, 2001.
c) Kick CH, et al. "Fluorine in Animal Nutrition";
Bulletin 558, Ohio Agricultural Experiment Station; Wooster, Ohio;
November 1935; pp 1-77.
d) Zipkin, I et al. "Urinary Fluoride Levels Associated
with Use of Fluoridated Water"; Pub Hlth Rpts 71 PP 767-772; 1956.
e) Manocha SL, et al. "Cytochemical response of
kidney, liver and nervous system to fluoride ions in drinking water";
Histochemical Journal, 7 (1975); 343-355.
f) On February 7, 2001, the Brookhaven Registry
of Enzymes listed 7,164 enzymes on their web-site, http://www.biochem.ucl.ac.uk/bsm/enzymes/
g) Dementi, B. "Cholinesterase Literature Review
and Comment"; Pesticides, People and Nature; 1 (2); 59-126; 1999.
h) Letter to the Honorable Ken Calvert, Chairman
of the Subcommittee on Energy and the Environment, US House Committee
on Science, from EPA Assistant Administrator J. Charles Fox, June
23, 1999.
i) Laylander, J. "A Nutrient/Toxin Interaction
Theory of the Etiology and Pathogenesis of Chronic Pain-Fatigue
Syndromes: Parts I & II," Journal of Chronic Fatigue Syndrome; 5(1),
67-126, 1999.
Synopsis of Foreward Authors' Relevant
Professional History
Roger D. Masters, Ph.D., is President of
the Foundation for Neuroscience and Society and Nelson A. Rockefeller
Professor of Government Emeritus at Dartmouth College. For the last
30 years, he has studied the implications of modern biological science
in understanding human behavior. He serves as editor of the "Biology
and Social Life" section of Social Science Information (an
international journal published at the Maison des Sciences de l'Homme
in Paris) and member of the Council of the Association for Politics
and the Life Sciences. He is a published expert in the history of
Renaissance politics, especially the contribution of Niccolo Machiavelli.
After undergraduate studies at Harvard (where his
instructors included Henry Kissinger), he served in the US Army
before graduate studies at the University of Chicago. Despite his
work in other areas, he retained a strong professional interest
in military and international affairs. In addition to writing The
Nation is Burdened: American Foreign Policy in a Changing World
(Knopf, 1967), he served as US Cultural Attache to France. Among
his many other books are The Political Philosophy of Rousseau (Princeton,
1968), The Nature of Politics (Yale, 1989), Machiavelli, Leonardo,
and the Science of Power (Notre Dame Press, 1996) and Fortune is
a River: Leonardo da Vinci and Niccolo Machiavelli's Magnificent
Dream to Change the Course of Florentine History (Free Press, 1998).
Before turning to issues of environmental pollution, health and
behavior, he also published widely on the effectiveness of leaders'
nonverbal behavior on television (working with colleagues on experiments
in France and Germany as well as in the US).
Among many other publications on biological factors
in human behavior, he was co-editor (with Michael T McGuire) of
The Neurotransmitter Revolution, Serotonin, Social Behavior and
the Law (Southern Illinois University Press, 1994); senior author
(with Brian Hone and Anil Doshi) of "Environmental Pollution,
Neurotoxicity, and Criminal Violence," in J. Rose, ed., Aspects
of Environmental Toxicity (London: Gordon & Breach, 1998), pp.
13-45; and co-author (with MJ Coplan) of "Water Treatment with
Silicofluorides and Lead Toxicity," International Journal of
Environmental Studies, 56: 435-449 (July-August 1999) as well as
of other publications.
In addition to an earlier teaching position in
political science at Yale, he served as US Cultural Attache to France,
Fellow of the Hastings Center, Chair of the Executive Committee
of the Gruter Institute for Law and Behavioral Research (a foundation
specialized in linking biology to the study and practice of law),
a visiting professor at Yale Law School and Vermont Law School,
and a consultant to Upjohn Corp, to the Commissioner of Corrections
of Vermont, and to several agencies of the Federal Government. As
a result of these varied professional activities, Dr. Masters has
had extensive experience applying new scientific research in biology
of human behavior to the establishment of successful government
policies.
Myron J. Coplan, PE is a consultant in chemical
engineering and chemical sciences, doing business at "Intellequity"
after retirement in 1987 as Vice President and General Manager of
the Albany International Co. Membrane Development Venture. The fruits
of this latter activity include a product line of membranes now
used by a major multi-national company to supply a market for industrial
gases measured in the $ billions.
Coplan's working career started during WWII first
as a civilian employee of the US War Department and then as a production
chemist for a firm supplying the military with two crucial commodities:
DDT, without which the S. Pacific campaign might not have been successful,
and a wire insulating chemical, without which the US Navy's capacity
to deal with disastrous convoy damage by Nazi mines might not have
been achieved. He was one of the few civilians deferred throughout
WWII for his critical occupation status.
Post WWII, while pursuing his own advanced degree
studies, Coplan headed an academic chemical engineering department,
supervising doctoral research of others. This was followed by a
37-year relationship with an independent consulting and r/d firm
specializing in material sciences (chemistry, polymer systems, statistical
analysis, physics, fluid dynamics, statistical mechanics, etc.)
which eventually became the central research laboratory of a large
multinational corporation.
Coplan is recognized in American Men of Science,
holds 32 patents, is a member of several professional organizations
and has published many technical papers. He authored a series of
bench-mark articles on mathematical probability statistics and wrote
a manual on statistical quality control for internal corporate use.
He also personally carried out a wide range of laboratory research
and engineering tasks and supervised the work of as many as 35 other
professionals of many disciplines. He has been consulted by research
staffs and corporate executives from some of the world's largest
corporations. To mention only one example, over about ten years
he had 28 assignments from GE.
His services were also engaged by NASA, USDA, EPA,
Interior Dept, Post Office Dept and several other government agencies,
including virtually every branch of the DOD. In these assignments,
Coplan was cleared on a "need-to-know" high level security
basis several times for consulting and research work in such diverse
fields as "decoy" chaff used to frustrate radar-tracked
anti-aircraft fire to protective measures for ground-troops at risk
of exposure to chemical, biological and nuclear attack.
In due course, Coplan's activities became more
focused on the interests of the large company which in 1972 had
acquired the firm he had joined in 1951. After 1972, he took on
the corporate mission of identifying and exploiting science-based
new business opportunities, including direct management of scientific
entrepreneurial r/d for new products and technologies. He became
Senior Corporate Scientist and then Vice President and General Manager
of a membrane development venture that eventually licensed his patented
inventions to other large corporations. Membrane treatment of phosphate
waste pond waters was among the applications studied. Coplan, therefore,
has first-hand knowledge of the processes from which the principal
water fluoridating agents (the silicofluorides) are derived.
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